Guidelines for supply and constraint measure …€¦ · Web viewPhase 2 Assessment Guidelines for Supply and Constraint Measure Business Cases Table of Contents APPENDICES3 ACRONYMS4

Phase 2 Assessment Guidelines for Supply

and Constraint Measure Business Cases

Table of ContentsAPPENDICES......................................................................................................................3

ACRONYMS.........................................................................................................................4

1 Introduction.......................................................................................................................5

2 Business Case Development and Assessment Process..................................................6

2.1 Steps and Timeframes to Develop and Assess Business Cases..............................6

2.2 Roles and responsibilities..........................................................................................8

3 Eligibility Criteria.............................................................................................................10

3.1 Supply Measure Requirements...............................................................................11

3.1.1 Supply measure definition................................................................................11

3.1.2 Measures not included in the benchmark conditions of development..............11

3.2 Constraint Measure Requirements..........................................................................11

3.2.1 Constraint measure definition...........................................................................11

3.2.2 Alignment with the Constraints Management Strategy (CMS).........................12

3.3 Operational by 30 June 2024...................................................................................12

3.4 Eligibility for Commonwealth Supply or Constraint Measure Funding.....................12

3.4.1 The measure is a ‘new measure’......................................................................12

3.4.2 Compliance with the purposes of the Water for the Environment Special Account (Constraint measures only).............................................13

4 Information Requirements for Preparing and Assessing Business Cases.....................13

4.1 Project Details..........................................................................................................13

4.2 Ecological values of the site....................................................................................14

4.3 Ecological objectives and targets............................................................................17

4.4 Anticipated ecological outcomes.............................................................................18

4.4.1 Anticipated ecological benefits.........................................................................18

4.4.2 Potential adverse ecological impacts...............................................................19

4.5 Hydrology of the area and environmental water requirements................................19

4.5.1 Current hydrology and proposed changes to the hydrology.............................19

4.5.2 Environmental water requirements...................................................................21

4.6 Operating regime.....................................................................................................23

4.7 Assessment of risks and impacts of the operation of the measure.........................23

4.8 Technical feasibility and fitness for purpose............................................................24

4.9 Complementary actions and interdependencies.....................................................25

4.10 Costs, Benefits and Funding Arrangements............................................................26

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4.10.1 Projects seeking Commonwealth Supply or Constraint Measure Funding......26

4.10.2 Projects not seeking Commonwealth Supply or Constraint Measure Funding 27

4.11 Project Governance and Project Management Arrangements................................27

4.11.1 Stakeholder management strategy...................................................................27

4.11.2 Legal and regulatory requirements...................................................................28

4.11.3 Governance and project management.............................................................29

4.11.4 Risk assessment of Project Development and Delivery...................................30

APPENDICES

1 – Expected steps and timeframes to develop and assess business cases

2 – Diagram of assessment process after submission of business cases to SDLAAC

3 – Sustainable Diversion Limit adjustment mechanism governance diagram

4 – Purposes of the Water for the Environment Special Account (s.86AD Water Act 2007)

5 – Summary table of eligibility criteria and information requirements for developing and assessing business cases

6 – Summary of key evaluation criteria

7 – Guidance on information required to support modelling and analysis

8 – Categories of risk and impact that should be considered in business case development

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ACRONYMS

The Basin Plan The Murray‒Darling Basin Plan adopted by the Commonwealth Minister under section 44 of the Water Act 2007 (Cth) on 22 November 2012

BOC Basin Officials Committee

CEWH Commonwealth Environmental Water Holder

CEWO Commonwealth Environmental Water Office

CMS Constraints Management Strategy

Department Commonwealth Department of the Environment

ESLT Environmentally Sustainable Level of Take

ESLT report The proposed ‘environmentally sustainable level of take’ for surface water of the Murray–Darling Basin: Method and outcomes (November 2011)

GIS Geographic Information System

GST Goods and Services Tax

Guidelines Phase 2 Assessment Guidelines for Supply and Constraint Measure Business Cases

HIS Hydrological Indicator Site

IGA Intergovernmental Agreement on Implementing Water Reform in the Murray‒Darling Basin

IGA Protocol Schedule 1 to the IGA (Protocol for consideration of surface water Sustainable Diversion Limit (SDL) adjustment measures)

MDB Murray‒Darling Basin

MDBA Murray‒Darling Basin Authority

RiMFIM River Murray Floodplain Inundation Model

SDL Sustainable Diversion Limit

SDLAAC Sustainable Diversion Limit Adjustment Assessment Committee

SDLATWG Sustainable Diversion Limit Adjustment Technical Working Group.

SFIs Site-specific Flow Indicators

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1 Introduction

The Intergovernmental Agreement on Implementing Water Reform in the Murray‒Darling Basin (the IGA) sets out three phases for the Sustainable Diversion Limit Adjustment Assessment Committee (SDLAAC) to evaluate supply and constraint measures: feasibility studies (Phase 1), business cases (Phase 2), and confirmation of projects (Phase 3). To guide the development of constraint and supply measure proposals and to ensure a consistent approach in assessing proposals, the IGA identifies the need for assessment guidelines to be developed for each of the three phases.

The purpose of Phase 1 was to identify the measures that could deliver a Sustainable Diversion Limit (SDL) adjustment or improve the effectiveness of environmental water delivery, that warrant consideration for development of a business case for assessment under Phase 2.

The purpose of the Phase 2 Assessment Guidelines for Supply and Constraint Measure Business Cases (the guidelines) is to guide the development and assessment of business cases for proposed supply and constraint measures.

The guidelines provide information and guidance in two key areas:

1. what is expected of proponent jurisdictions in developing business cases (including standards, information requirements and minimum specifications); and

2. the process for assessing business cases, including roles and responsibilities for conducting assessments; eligibility criteria to be used when assessing proposals; and timeframes for developing, submitting and assessing business cases.

Business cases will form the basis of advice for due diligence and executive decision making on investments. Business cases need to include consideration of alternative solutions to the preferred project; identify assumptions, benefits, costs and risks; and provide a compelling case for investment in the preferred option (IGA Protocol, clause 28).

The guidelines recognise the different information needs for each category of supply and constraint measure project:

Environmental works and measures at point locations: These infrastructure-based measures attempt to directly achieve the Basin Plan’s environmental outcomes at specific sites along the river using less environmental water than would otherwise be required.

Water efficiency projects: These infrastructure-based measures achieve water savings by reducing water losses through, for example, modified wetland or storage management.

Operating rules changes: Changes to policies and operating rules can lead to more efficient use of water and savings which can contribute to achieving equal environmental outcomes with less water.

Physical constraint measures: These measures ease or remove physical constraints on the capacity to deliver environmental water.

Operational and management constraint measures: These measures change river management practices (e.g. policies, procedures and protocols that are outlined in legislation,

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intergovernmental agreements, water resource plans, river operating manuals and procedures and guidelines, as well as unwritten practices) that currently act as constraints on the capacity to deliver environmental water.

A measure may fall directly within one of these categories or potentially may combine elements of different categories into one measure.

All projects that wish to be considered at Phase 2 need to submit a business case that is consistent with these guidelines. Proponents of projects that have already been approved through another process (e.g. The Living Murray projects) should make an assessment as to which sections of the guidelines are relevant. The guidelines also recognise the differing information needs, depending on whether or not the projects are seeking Commonwealth Supply or Constraint Measure Funding.

Proponents may be asked to provide additional information not specified in these guidelines if it is deemed necessary for the assessment of a measure by SDLAAC or the Basin Officials Committee (BOC).

These guidelines do not apply to efficiency measures. Note that an efficiency measure is defined in Chapter 7 of the Basin Plan as a measure that operates to decrease the quantity of water required for one or more consumptive uses in a set of surface water SDL resource units, compared with the quantity required under the benchmark conditions of development. Examples include lining channels to reduce water losses within an irrigation network or replacement of less efficient irrigation methods with drip irrigation.

2 Business Case Development and Assessment Process

2.1 Steps and Timeframes to Develop and Assess Business Cases

Schedule 1 to the IGA (the IGA Protocol) establishes a process for the assessment of business cases and progression of projects to Phase 3 (cl. 28). Clause 28 states that ‘all Phase 2 Assessments are expected to be completed by 30 June 2015’. Key steps in the process are:

1. Jurisdictions prepare and submit Phase 2 business cases to SDLAAC;

2. Early information is provided to Murray‒Darling Basin Authority (MDBA) to support its analysis;

3. SDLAAC assesses individual business cases;

4. MDBA undertakes preliminary analysis of proposals; and

5. SDLAAC and BOC determine the package of projects to proceed to Phase 3.

Refer to Appendix 1 for a graphic of the expected steps and timeframes to develop and assess business cases. Appendix 2 contains a flow diagram of assessment processes after submission of business cases to SDLAAC.

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Jurisdictions prepare and submit business cases

Jurisdictions will prepare business cases with technical assistance from the MDBA and submit business cases progressively to SDLAAC. The anticipated timeframe for business case submissions is 31 December 2014. Business cases may be submitted after this date, recognising that late submissions:

may not be included in the MDBA’s preliminary analysis; and

may cause difficulties for SDLAAC to complete Phase 2 by 30 June 2015, particularly if further information is to be provided by proponents.

Jurisdictions will prioritise the development of business case during 2014 with the assistance of the SDL Adjustment Technical Working Group (SDLATWG). The aim of prioritisation is to assist the participating jurisdictions and the MDBA to devote time and resources to developing and appraising the most prospective proposals. Following the prioritisation of measures, proponents and the MDBA will work collaboratively to capture and deliver information to:

assist proponents develop business cases; and

represent proposed measures in hydrologic models.

SDLAAC assesses individual business cases

Each constraint and supply measure that advances to Phase 2 will be individually assessed by SDLAAC (cl.28 IGA Protocol). Assessments will be progressive as business cases are submitted.

In assessing business cases, jurisdictions may draw on independent technical or financial expertise as deemed appropriate to ensure robust due diligence is performed. SDLAAC may also request additional information from proponents as deemed appropriate.

Where Commonwealth Supply or Constraint Measure Funding has been requested, the Commonwealth will assess the suitability of measures for Commonwealth Funding against the criteria contained in these guidelines, at the same time as assessing the business cases as a member of SDLAAC. The information requirements and evaluation criteria for Commonwealth due diligence are no different to the requirements set out in these guidelines. However, it is important to note that successful completion of the Phase 2 assessment does not constitute conditional funding approval for measures. Such approval can only be given by the Commonwealth Minister with responsibility for water. This will occur in Phase 3 (Confirmation).

MDBA analysis

MDBA will undertake an analysis on each business case as soon as practicable after submission, subject to agreed prioritisation.

The MDBA will analyse the package of business cases submitted by 31 December 2014 and provide advice to SDLAAC as required under the IGA. This advice will be without prejudice and where possible will be informed by modelling. The main aim of the MDBA’s analysis will be to provide an initial indication of:

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the potential benefits and dependencies between measures; and

an indicative impact of the measures on the SDL reduction amount, potential environmental outcomes, impacts on state water shares and States’ water resources (cl.28 IGA Protocol).

In undertaking this work, where possible and relevant the MDBA will analyse specific characteristics of the proposed measures, including:

ability to deliver water efficiency savings;

ability to deliver Basin Plan environmental objectives;

potential ecological benefits;

potential risks and adverse impacts, including those associated with downstream water users, state water shares and states’ water resources (including reliability and quality); and whether risks are adequately addressed;

analysis of how the proposed measure has given regard to water quality and salinity targets described by the Basin Plan;

likely harmonisation or interdependencies with other measures;

net evaporative savings;

other analysis as required; and

an initial analysis of the likelihood that the package will achieve environmental equivalence.

The MDBA will undertake analysis of the information that is provided progressively in accordance with the prioritisation and information guidelines. MDBA will provide the results of this technical analysis by 31 May 2015.

This analysis will only include those business cases which are submitted to SDLAAC in time to be analysed.

SDLAAC and BOC determination of the package of measures to proceed to Phase 3

By 30 June 2015, SDLAAC will consider the assessment reports from individual SDLAAC members and the MDBA advice, and determine the package of project proposals that will advance to Phase 3. This package will be recommended to BOC for approval.

2.2 Roles and responsibilities

Roles and responsibilities in the development, analysis and assessment of supply and constraint measure business cases are summarised below. An overview of the SDL Adjustment Mechanism governance arrangements is included at Appendix 3.

Basin states

Basin states officials participate as members on SDLAAC and BOC and are responsible for consulting with stakeholders and developing business cases, including responding to any requests for additional information from SDLAAC or BOC.

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The Basin states are committed to working in a collaborative and iterative manner with the MDBA to ensure a high quality technical input to the development of business cases.

SDLAAC / BOC

SDLAAC is responsible for assessing proposed supply and constraint measures in accordance with the IGA Protocol (cl.13 IGA Protocol) and making recommendations to BOC. SDLAAC members will review business cases in accordance with these guidelines and record their advice and recommendations, including rationale, for advancing proposals to Phase 3 (Confirmation).

When assessing proposals, SDLAAC or BOC may request additional information from the proponent or further advice on particular matters by the MDBA or others, including independent technical or financial expertise as deemed appropriate.

BOC is responsible for deciding which proposals recommended by SDLAAC advance to Phase 3 (Confirmation).

MDBA

The MDBA is a non-voting participant on SDLAAC. MDBA will undertake an initial analysis on a package of projects at the end of Phase 2, as described above, in consultation with the SDLATWG. MDBA will also provide advice to proponent jurisdictions to assist development of business cases, regarding:

integration of the scoring method and testing of SDL adjustment methodology within the modelling framework; and

the development of model functionality to assist with business case development (most notably those related to the River Murray model).

Where appropriate the MDBA may also undertake modelling in circumstances where this cannot be undertaken by another organisation and is required for business case development

Commonwealth Department of the Environment (the Department)

The Department represents the Commonwealth at SDLAAC and BOC. The Department is also responsible for assessing supply and constraint measures where Commonwealth Supply or Constraint Measure Funding is sought and making funding recommendations to the relevant Commonwealth Minister with responsibility for water. The information requirements and evaluation criteria for Commonwealth due diligence are the same as the requirements set out in these guidelines. Commonwealth due diligence assessment may draw on independent technical or financial expertise as the Department deems appropriate.

Commonwealth Environmental Water Office (CEWO)

The CEWO is a non-voting participant on SDLAAC. The CEWO will provide advice on the assessment and prioritisation of supply and constraint measure projects, based on the practical experience of delivering environmental water across the Murray‒Darling Basin. Proponent jurisdictions need to actively engage with the CEWO in the development of projects that relate to rule changes and to river operation, particularly those that may need environmental water in order to implement the proposed change.

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SDL Adjustment Technical Working Group (SDLATWG)

The SDLATWG has been set up as the successor to the Benchmark Modelling Working Group and Ecological Elements Inter-jurisdictional Technical Reference Committee. The SDLATWG will provide advice to SDLAAC on technical matters relating to implementation of the jurisdictional assessment process and SDL adjustment mechanism including:

development and application of the ecological elements method and benchmark model, including the integration of the ecological elements method and benchmark modelling;

the technical assessment of SDL adjustment and constraints projects to support jurisdictional decision making (including MDBA approaches/methods for providing technical information and advice);

criteria for ranking and prioritising the development of SDL adjustment and constraint measures for assessment;

the key information and timing required to assist states and MDBA to model proposals;

technical advice to assist SDLACC in assessing an initial suite of measures at the conclusion of Phase 2; and

other matters as requested by SDLAAC.

The SDLATWG will act as a forum for jurisdictions and the MDBA to work constructively and collaboratively to discuss and address modelling and SDL adjustment method development issues and progress the development and technical analysis of SDL adjustment and constraint measures.

3. Eligibility Criteria

Eligibility criteria are overarching criteria that are expected to be met to determine whether a proposed measure meets Basin Plan and IGA requirements for further assessment and consideration in the SDL adjustment mechanism:

all supply measure projects must satisfy the requirements of criteria 3.1 and 3.3;

all constraint measure projects must satisfy the requirements of criteria 3.2 and 3.3; and

to be considered for Commonwealth Supply or Constraint Measure Funding, a supply measure must also meet criterion 3.4.1 and a constraint measure must meet criteria 3.4.1 and 3.4.2.

If the business case does not satisfy all relevant eligibility criteria, the measure will be assessed as ineligible and no further assessment will be undertaken.

The eligibility criteria will be assessed on the basis that the business case demonstrates that each relevant requirement is met. For example, the business cases may provide a table that indicates where in the body of the business case those relevant eligibility criteria have been met. This section does not require duplication of information requested in Section 4.

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3.1 Supply Measure Requirements

3.1.1 Supply measure definition

This criterion reflects the definition of ‘supply measure’ under the Basin Plan (cl.7.03 and (cl.7.15). The measure must:

operate to increase the quantity of water available to be taken in a set of surface water SDL resource units compared with the quantity available under the benchmark conditions of development;

achieve equivalent environmental outcomes with a lower volume of held environmental water than would otherwise be required; and

have no detrimental impacts on reliability of supply of water to holders of water access rights that are not offset or negated.

The business case will need to provide evidence that the measure has potential to be a supply measure as per this definition, noting that a final determination will require MDBA modelling. MDBA will undertake modelling of each business case as soon as practicable after submission, subject to agreed prioritisation. If the business case does not satisfy this criterion, the measure cannot proceed to Phase 3.

3.1.2 Measures not included in the benchmark conditions of development

The measure must not be an ‘anticipated measure’ (cl.7.12 (3)(b) of the Basin Plan). In order for the measure to satisfy the criterion, the proponent must confirm that the measure was not in the benchmark conditions of development (cl.7.02 of the Basin Plan). Benchmark conditions include the infrastructure, rules and practices that were assumed in the benchmark model, including certain measures that were not yet in effect but were expected to be in place by 2019 (cl.7.02 of the Basin Plan). MDBA is preparing a benchmark conditions of development report (expected to be released in 2014) to assist proponents.

3.2 Constraint Measure Requirements

3.2.1 Constraint measure definition

This criterion reflects the definition of ‘constraint measure’ under the Basin Plan (cl.7.02 and cl.7.09). The measure must:

remove or ease a physical or other constraint on the capacity to deliver environmental water to the environmental assets of the Murray‒Darling Basin; and

when combined into a package of supply, efficiency and constraint measures, allow environmental water to be used to maximum effect.

In order for the measure to satisfy the criterion, the proponent will have to demonstrate that the measure has potential to remove or ease a constraint on environmental water delivery and to allow environmental water to be used to maximum effect.

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The business case must also indicate how the measure allows the enhanced environmental outcomes as set out in Schedule 5 (cl.7.09 (e)) to be pursued compared to the benchmark environmental outcomes.

3.2.2 Alignment with the Constraints Management Strategy (CMS)

The development and prioritisation of constraint measures must be undertaken having regard to the CMS prepared by the MDBA under cl.7.08 of the Basin Plan (cl.21 IGA Protocol). In order for the measure to satisfy the criterion, the proponent will have to demonstrate consistency with the CMS.

3.3 Operational by 30 June 2024

This criterion reflects the requirement of the Basin Plan and the IGA Protocol that all supply and constraint measures must be ready to enter into operation by 30 June 2024 (cl.7.12 of the Basin Plan and Table 1 of the IGA Protocol). In order for the measure to satisfy the criterion, the proponent will have to demonstrate that the measure will be designed and implemented to enter into operation by 30 June 2024. The business case must also state the date on which the measure either entered into operation (existing measures) or by which it is expected to enter into operation (new measures) (cl.7.12(4)(d) of the Basin Plan).

3.4 Eligibility for Commonwealth Supply or Constraint Measure FundingIf the proponent proposes to seek Commonwealth Supply or Constraint Measure Funding, the proponent will need to satisfy the criteria below. These criteria do not apply if the proponent is not seeking Commonwealth Supply or Constraint Measure Funding.

3.4.1 The measure is a ‘new measure’

This criterion is used to assess whether the measure is eligible to be considered for full or partial Commonwealth Supply or Constraint Measure Funding. This funding will not be provided for projects:

where full funding has already been provided or committed by the Commonwealth (such as pre-existing Commonwealth funded projects); or

that have already been approved for funding by another organisation.

In order to satisfy the requirements of this criterion, the proponent will need to confirm that the measure has not received funding from any other source. Where the proposed measure has been partially funded from another source, the proponent will need to detail the amount and source of the funds received or proposed to be received.

If the business case cannot satisfy the requirements of this criterion, it will be assessed as ineligible for Commonwealth Supply or Constraint Measure Funding. It may nevertheless remain eligible as a measure to be included in the SDL adjustment mechanism.

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3.4.2 Compliance with the purposes of the Water for the Environment Special Account (Constraint measures only)

This criterion is used to assess whether a constraint measure is eligible for Commonwealth Constraint Measure Funding under the Water for the Environment Special Account.

If the proponent proposes to seek funding for the constraint measure from the Water for the Environment Special Account, the business case will need to demonstrate that the measure aligns with one of the purposes set out in s.86AD of the Water Act 2007 (Cth) (see Appendix 4). If the measure does not satisfy this criterion, it will be assessed as being ineligible for consideration for Commonwealth Constraint Measure Funding from the Water for the Environment Special Account. It may nevertheless be eligible to be included in the SDL adjustment mechanism as a constraint measure. This criterion does not apply to supply measures.

4. Information Requirements for Preparing and Assessing Business Cases

The following section details the information requirements that are to be provided in a supply or constraint measure business case. This information will allow SDLAAC to assess individual project business cases, assist the MDBA to conduct a preliminary analysis of an initial suite of proposed measures at the end of the business case phase, and inform SDLAAC and BOC’s determination of the package of measures to proceed to Phase 3.

While not all requirements may be relevant for all projects, it is recommended that all requirements are considered and where not relevant this is stated in the business case with the associated rationale.

Appendix 5 provides a high level summary of which sections are relevant to each supply and constraint measure project type. Appendix 6 provides a summary table of the key evaluation criteria which will be used by SDLAAC to assess projects.

Reports need to be referenced appropriately throughout the business case and a bibliography of referenced reports included in the business case.

4.1 Project Details

All business cases need to provide an overview of the project that contains, as a minimum, the following:

description of proposed measure, including locality map;

name of proponent and proposed implementing entity;

summary of estimated costs and proposed schedule; and

definition of the measure within one of the follow categories:

o environmental works and measures at point locations;

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o water efficiency projects;

o operating rules changes;

o physical constraint measures; or

o operational and management constraint measures.

4.2 Ecological values of the site

If relevant, the business case needs to include a description of the ecological values and features of the site that will be influenced by the proposed measure, including:

a description of key water-dependent and floodplain vegetation and habitat types;

water-dependent flora and fauna species present at the site;

the identification of important plant, bird, fish, and frog species, including any significant, threatened or listed species/communities;

whether the site is formally recognised in any international agreements (e.g. Ramsar wetland of international importance) or as an area of conservation significance (e.g. by a state government);

an assessment of the vital ecological functions of the site; and

an assessment of the site as providing vital habitat, including:

o a refugium for native water-dependent biota during dry spells and drought;

o pathways for the dispersal, migration and movements of native water-dependent biota; or

o important feeding, breeding and nursery sites for native water-dependent biota.

The business case needs to include a description of the current ecological condition of the site (e.g. whether the site is highly modified) and an overview of past management activities and actions. The proponent may include a GIS vegetation and land-use layer as part of the business case.

The purpose of providing this information is to establish the ecological rationale for the proposed measure (IGA Protocol Table 1), and assist SDLAAC to understand the ecological significance of the site.

Procedure to assess information

The business case will be assessed on the basis that the description of the ecological values and features of the site is:

of a similar standard to the descriptions of ecological values and features found in Environmental Water Management Plans for Living Murray Icon Sites; and

supported by relevant information from investigations of the site, including from published and unpublished scientific studies; environmental management plans; environmental water requirement reports; flora and fauna databases including those for threatened species; surveys; maps; and photos.

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Text from the Chowilla Floodplain Environmental Water Management Plan 2012 are provided below as examples to assist proponents to understand the type of information sought, noting that they do not cover all of the information requirements listed above.

Fauna

‘The diverse vegetation assemblages and the variability of the riverine environment create a mosaic of differing habitat types that vary in time and space in response to changing river flows. This creates distinct aquatic and terrestrial fauna assemblages that include threatened species listed at both a national and state level. Three species have been listed as vulnerable under Environment Protection and Biodiversity Conservation Act 1999 (Cwlth) — the regent parrot (Polytelis anthopeplus), the southern bell frog (Litoria raniformis) and the Murray cod (Maccullochella peelii). Species listed under the National Parks and Wildlife Act 1975 (SA), the Threatened Species Conservation Act 1995 (NSW) and the Fisheries Management Act 1994 (NSW) include four mammals, five reptiles, one amphibian, five fish and 20 bird species’.

‘Wetlands in the Chowilla Floodplain also provide seasonal habitat for migratory birds listed under the following international agreements: Japan–Australia, China–Australia and the Republic of Korea – Australia Migratory Bird Agreements’.

‘The Chowilla anabranch and floodplain system provide flowing water habitats for native fish that are now poorly represented in the South Australian are now poorly represented in the South Australian section of the River Murray. This system supports 11 species of native fish, including a breeding population of the federal Environment Protection and Biodiversity Conservation Act-listed Murray cod and five species listed under the Fisheries Management Act (NSW) including silver perch (Bidyanus bidyanus), freshwater catfish (Tandanus tandanus) and the crimson-spotted rainbowfish (Melanotaenia splendida fluviatilus)’.

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Flora

‘Chowilla’s vegetation communities are distributed across the floodplain and upland rise according to local hydrological conditions that include environmental watering actions, soil type and salinity gradients, while the floristic composition of aquatic and littoral communities strongly correlates with current velocity (Roberts & Ludwig 1991). The major vegetation communities of the floodplain are:

river red gum forest and woodlands

black box woodlands

lignum (Muehlenbeckia florulenta) low shrubland (SA Department for Environment and Heritage 2010).

Kenny (2004) delineated over 40 broad vegetation associations for the Chowilla Floodplain based on overstorey dominance and structural similarity. These associations are presented in Figure 2.3. Black box woodland is the most widespread vegetation class, occupying approximately 5,117 ha (29%) of the Chowilla Floodplain (CSIRO 2005)’.

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4.3 Ecological objectives and targets

If relevant, a description of the ecological objectives and targets needs to be included in the business case.

Ecological objectives need to include overarching objectives, as well as more specific objectives and targets for vegetation, waterbirds, fish and other water-dependent species where relevant. Ecological objectives and targets need to be specific, relevant, measurable and achievable. The objectives need to be supported by relevant scientific references, investigation reports, scientific reports and surveys.

Site based proposals should use the relevant ecological information to set site-based flow objectives and targets. If applicable, information about how ecological objectives for projects are related to site-specific ecological targets sought by the Basin Plan should be supplied. This will enable SDLAAC to understand how the objectives of the project relate to objectives and targets in the Basin Plan.


The business case will be assessed on the basis that the ecological objectives and targets provided:

are clearly articulated;

represent the ecology of the site;

are consistent with the Basin Plan (e.g. they reflect the objectives and targets in the Basin Plan, and supporting documentation, and are supported by scientific evidence);

are quantified where it is appropriate to do so;

take into account interaction and inter-dependencies with other supply measures (to the extent possible prior to modelling by the MDBA that combines proposals);

take into account ecosystem function, connectivity, interaction and inter-dependencies with other sites/habitats across the reach;

are supported by evidence such as scientific reports, surveys, mapping/modelling; and

compare the frequency, extent and duration of watering of the proposed measures with:

o the natural flow regime; and o under the Basin Plan without the measure.

Matters to be considered in the assessment include:

the overarching objectives in Schedule 7 of the Basin Plan;

the site-specific objectives and targets listed in Appendix D of The proposed ‘environmentally sustainable level of take’ for surface water of the Murray–Darling Basin: Method and outcomes (November 2011) (ESLT report); and

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other work to develop ecological objectives and targets (e.g. development of objectives and targets for priority environmental assets in State long-term watering plans under cl.8.19 of the Basin Plan; Icon site environmental water management plans).

Examples of ecological objectives and targets are included in the text box below:

A specific ecological objective relevant to the Riverland-Chowilla floodplain hydrologic indicator site (HIS) is to: protect and restore biodiversity that is dependent on Basin water resources, including by ensuring that representative populations and communities of native biota are protected and, if necessary, restored.

A refined site-specific ecological objective by functional group is:

Vegetation

(1) Maintain viable river red gum populations with 70% (2,414 ha) of river red gum woodland

A site-specific ecological target for the Riverland-Chowilla floodplain HIS is to: provide a flow regime which ensures the current extent of the native vegetation of the riparian, floodplain, and wetland communities is sustained in a healthy and resilient condition. This is translated into a flow target. For example 40,000 ML/d for 30 days between June and December.

4.4 Anticipated ecological outcomes

If relevant, a business case needs to provide an analysis of the anticipated ecological benefits and impacts that are likely to result from the proposal.

4.4.1 Anticipated ecological benefits

The current condition of the site (e.g. whether the site is highly modified) and an overview of past management activities and actions to demonstrate the potential for the proposal to achieve its intended environmental outcomes/benefits needs to be included in the business case.

The description of benefits needs to consider significant, threatened or listed species and communities and whether any matters of environmental significance are affected. For example, the business case might consider whether the site is formally recognised in any international agreements (e.g. Ramsar wetland of international importance) or as an area of conservation significance (e.g. by a state government).

Any assumptions used when developing the anticipated benefits need to be identified, including advice on how the operation of the project is likely to bring about the environmental benefits.

Proponents also need to provide a monitoring and evaluation plan to identify how progress will be monitored and to assess success in meeting the ecological objectives and targets.


The business case will be assessed on the basis that it:

includes an ecological assessment that is detailed enough to provide a clear picture of the likely ecological benefits of the project, including some quantitative assessment where this is

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possible (e.g. estimate of additional area inundated for different ecosystem components; or expected number of additional inundation events); and

is supported by relevant investigations, scientific studies, environmental management plans, and flora and fauna databases etc.

4.4.2 Potential adverse ecological impacts

If relevant, business cases need to include an assessment of potential adverse ecological impacts resulting from the operation of the proposed measure. At a minimum, potential impacts to be addressed include:

adverse salinity impacts or water quality outcomes either at the site or downstream (e.g. hypoxic blackwater events);

the potential to increase pest species (e.g. carp, weeds and rabbits);

the potential to favour certain species to the detriment of others or to adversely affect certain species;

adverse impacts on ecological function and connectivity; and

any potential cumulative impacts with other measures in the reach/river system.

The business case needs to outline how:

these potential impacts will be managed; or

if they cannot be managed, justify how the impacts are acceptable (i.e. a minor adverse impact that is outweighed by the environmental benefit).

The description of impacts needs to consider significant, threatened or listed species and communities and whether any matters of environmental significance are affected.


The business case will be assessed on the basis that:

an adequate assessment of potential adverse ecological impacts has been undertaken;

there is a demonstration that any adverse impacts can will be managed, mitigated or are managed to acceptable levels ; and

the assessment is supported by relevant investigations, scientific studies, environmental management plans, and/or flora and fauna databases etc.

4.5 Hydrology of the area and environmental water requirements

4.5.1 Current hydrology and proposed changes to the hydrology

If relevant to the proposal, proponents should clearly articulate the current hydrology of the system or site. This would include the current frequency, duration and timing of relevant flow events and, if possible, how these relate to inundation extent. MDBA can provide jurisdictions the spatial inundation (RiMFIM) output data for Site Specific Flow Indicators (SFIs) for each river reach.

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Where relevant, the business case needs to include a quantitative description of the proposed hydrology and hydraulic relationships at the site based on observed data, hydrodynamic models or other models that are suitable. The model chosen should take into account the complexity of the proposal. The MDBA can advise proponents further on model choice.

The business case needs to supply the following:

the relationship between flow in the river and inundation of the site. This is usually defined as a level, area, volume relationship, where level is the height of the river under all modes of operation;

where a proposal changes the flows in the river system, include a comparison of the flows under current conditions and the flows that result from the proposal (including flow that returns to the river).

any models used to represent the proposal and a copy of any software developed or used for assessment along with input and output files used to assess the proposal;

the results of any calibration and validation carried out for representation of the current conditions and of the proposed measure in the relevant model;

any additional modelling assumptions used to represent the measure in the relevant model in the absence of observed data to carry out the assessment;

spatial representation of the area inundated under various flow conditions and the vegetation types impacted for different levels of inundation;

for operating rule changes, any additional modelling assumptions used to represent the proposal in the model; and

the statistics output from the modelling framework (using post processing tools) to provide a consistent comparison of changes in relevant statistics across projects (as an appendix to the business case).

This information will assist SDLAAC to develop a broader understanding of the proposal and the likely changes resulting from the proposal in terms of hydrology. Appendix 7 contains further details of information requirements.


The business case will be assessed on the basis that SDLAAC can understand:

the hydrology and hydraulic relationships at the site (if relevant);

the volume of water used by the environment at the site;

the proportion of environmental water that returns to the river under current conditions and proposed changed hydrology;

the changes in flows that result from the proposal (where the proposal alters river flows);

the scale and level of detail of modelling is fit-for-purpose (and in the case of inadequacy of data, that the uncertainty of the estimates is quantified);

the assumptions used to represent the measure in the relevant model are documented; and

supporting evidence shows that the model is calibrated adequately.

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4.5.2 Environmental water requirements

If relevant, the business case needs to include a description of the environmental water requirements for key ecological components that the supply measure operation intends to achieve.

This includes the frequency and duration of events; seasonality, depth, and variability in duration of watering events; and the tolerable drying phase duration. The requirements need to effectively define the current hydrological regime and the gaps in the regime that the proposal is seeking to mitigate.

The business case needs to include details about how the environmental water requirements for the proposal relate to the ecological values and ecological objectives and targets for the site as described in the business case. The environmental water requirements need to be consistent with the ecology present at the site.


The business case will be assessed on the basis that the environmental water requirements:

are supported by scientific evidence;

are linked to the ecological values at the site and the objectives and targets described in the business case; and

the frequency at which different vegetation types will be inundated and the period of inundation can be clearly understood.

Examples of accepted practice for describing environmental water requirements can be found in the Living Murray Icon site Environmental Water Management Plans.

Examples from the Barmah–Millewa Forest and Chowilla Management Plans are below.

Example of an ecological objective and environmental water requirement from Barmah-Millewa

To meet the ecological objective for waterbirds (successful breeding events of thousands of colonial and migratory waterbirds in at least 3 years in 10), long floods (15–18 GL/d for four to five months) lasting through spring into early summer are required. This would ensure that a range of species could nest, breed and fledge chicks before water levels started to decline.

As well as ensuring that water depth is maintained under nesting colonies until chicks are fledged, sufficient food resources must be available to support chicks and adults. Nesting colonial waterbirds will travel to wetlands within a 20 km radius of their nest sites in search of food; the success of a breeding event therefore depends on the availability of food resources within travelling distance of breeding colonies (Reid 2006).

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Example of ecological objectives and environmental water requirements from Chowilla

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4.6 Operating regime

If relevant, the business case needs to provide information on the natural regime of watering events and the appropriateness of the operation of the measure. The natural regime needs to be given as an indicator of the vegetation tolerances under a natural watering regime.

The operating regime needs to include a brief explanation of the role of each operating scenario. For infrastructure-based measures, these scenarios need to explain how each structure will be operated depending on the incoming flows and dependent on the watering event that is to be achieved (e.g. natural flood, hybrid events, managed events and enhancement). This should include explanation of how the structure will be operated to manage risks and to avoid or manage any adverse impacts.

The business case needs to:

list an indication of preferred timings for events and the main outcomes (e.g. land inundated, environmental water used); and

a brief explanation of how any new works will be operated in relation to existing measures.

Information about the operation regime will support the business case by providing details of how the structure will be operated in order to meet the ecological objectives and targets as described above and to minimise impacts to third parties. The intent is to provide information to assist decision making about whether the project can deliver environmental equivalence and whether risks/impacts can be managed. The operating regime will not prescribe particular watering events or if a watering event is to occur.



it clearly describes the ecological justification for the operating regime;

the operating regime includes a brief explanation of the role of each major structure followed by the operating scenarios;

it lists the preferred timings for events and the main outcomes (e.g. land inundated, environmental water used);

it provides an explanation of how the new measure will be operated in relation to existing scenarios; and

it provides sufficient information to allow SDLAAC to evaluate the policy or rule change and identify key interdependencies (if relevant).

This should include explanation of how the structure will be operated to manage risks and to avoid or manage any adverse impacts.

4.7 Assessment of risks and impacts of the operation of the measure

All business cases need to include a risk assessment and risk management strategy for the proposed operating regimes or proposed operating rules changes. Appendix 8 includes the

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categories of risk and impact that need to, at a minimum, be considered. The identification of risks in any case needs to be rigorous and should not be limited by this list of categories.

Note that risk assessment has been divided into two sections in these guidelines. This section 4.7 relates to the risks and impacts that arise out of the operation of the measure as a supply or constraint measure. New projects should also complete section 4.11.4 which identifies the requirements for the identification and mitigation of risks that arise as a result of project development and delivery.

A risk management strategy needs to be developed which:

assesses the identified project delivery and operating risks;

details mitigation strategies to manage these risks; and

identifies residual risks after mitigation strategies are applied.

Where possible, the identification of risk needs to be supported by relevant modelling, investigations and studies, including scientific evidence. For example the assessment of risks to native fauna could draw from information and studies from other similar projects.

Risk assessment should consider the risks associated with modelling i.e. accuracy of input data and should include an explicit assessment of assumptions and their implications on modelled outcomes.

The risk framework needs to identify risks and then rate them based on the likelihood (probability of occurrence) and consequence (magnitude of potential impact) of each risk.



all significant operating risks and impacts have been identified and analysed, and robust treatments and mitigations proposed;

the risk management strategy complies with the AS/NZS ISO 31000:2009 Risk management—Principles and Guidelines; and

all residual risks are negligible or can be adequately mitigated.

4.8 Technical feasibility and fitness for purpose

Where relevant, the business case needs to establish that the project infrastructure is technically feasible. It is expected that the business case will address the following information requirements on technical feasibility:

design criteria used;

options analysis/sensitivity analysis of preferred option;

concept design drawings;1

estimate of costs and benefits (see section 4.10 for details); 1 Providing sufficient information to understand the operation, size and location of the works (as opposed to detailed engineering drawings).

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location of activities to be undertaken, access routes, footprint area etc;

geotechnical investigation results;

ongoing operational monitoring and record keeping arrangements;

what other alternative designs and specifications were considered, and why this design and specification was chosen;

reliance on other measures or other actions (see section 4.9); and

governance and funding arrangements for on-going operation and maintenance and management of any infrastructure (see section 4.10 and 4.11).

The business case needs to provide sufficiently detailed and clear information requirements to allow an independent expert assessment of the technical feasibility and fitness for purpose of the measure and potential to contribute to an SDL adjustment.

For rule changes and operational and management constraints, the business case needs to provide relevant information to establish that the proposed measure is achievable and likely to deliver the expected outcomes. For example, the business case might provide information that the proposed change is supported by relevant parties and necessary legislative or other changes can be implemented.



the proposal is able to deliver effectively on its stated outcomes and any proposed technology is assessed to perform as intended; and

the project delivery and operation is secure over the long term.

SDLAAC members will review the information provided and, if necessary, seek advice from other experts.

4.9 Complementary actions and interdependencies

All business case must:

indicate the surface water SDL resource units that are affected by the measure (Basin Plan cl.7.12) and how they are affected – this could be for SDL adjustment or it could be a risk or impact; and

identify other supply and/or constraint measures, and/or complementary actions relevant to the measure.

It is a Basin Plan requirement that supply measure proposals identify which constraint measures are relevant (cl.7.12) and it is an IGA Protocol requirement that all linkages and inter-dependencies between supply and constraint measures are detailed (cl.5 and Table 1).



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known complementary actions and interdependencies are identified, noting that some interdependencies will only become clear once the project is modelled as part of package of measures.

4.10 Costs, Benefits and Funding Arrangements

The IGA Protocol specifies that a business case must identify benefits and costs that support a compelling case for investment (cl.28, IGA Protocol). The business case must include a detailed estimate of financial cost and advice on proposed funding arrangements (Table 1, IGA Protocol).

4.10.1 Projects seeking Commonwealth Supply or Constraint Measure Funding

For new, previously unfunded supply and constraints projects that are seeking Commonwealth Supply or Constraint Measure Funding, a formal cost-benefit analysis is not required in the business case. This is because the main benefit (the SDL adjustment) cannot be reliably estimated in time for business case submission. However, to enable a thorough assessment of value for money for individual projects and to inform future funding decisions for a package of measures, the business case must provide:

a detailed estimate of the total cost of the project (GST exclusive) including administration and management, design and approvals. Where a contingency allowance is included in the costing, the amount or percentage of this allowance needs to be clearly shown. The level of risk or uncertainty for each project will dictate the level of contingency. However, the business case should not use contingency to cover insufficient investigation and planning or to cover potential changes in project scope. If the business case proposes a level of contingency that appears inconsistent (higher or lower) with the level of risk identified, this will be identified by SDLAAC in their assessment of proposals;

co-contributions (i.e. the business case needs to detail funding amounts to be provided by all financial contributors), including Commonwealth Supply or Constraint Measure Funding sought;

ongoing operation and maintenance costs and proposed financial responsibility for ongoing asset ownership costs and the agency which will undertake this role. This information needs to address the full range of future operating conditions, including consideration of climate change impacts and seasonal variation on operation and maintenance costs; and

a description of the expected environmental, social and economic costs and benefits, quantitative where possible, otherwise described qualitatively.

Note that Commonwealth Supply or Constraint Measure Funding does not include funding for operational and maintenance costs for measures.

Adherence to robust State Government cost estimation standards and/or guidelines for business cases would be considered appropriate if adequately described in the business case.



justification is provided in the business case that supports the rationale for the estimate of the total cost of the project;

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the level of contingency appears consistent with the level of risk identified (see section 4.7 and 4.11.4);

for supply measures, the information provided will be used by SDLAAC to assess cost effectiveness (surrogates may be used in this analysis – e.g. cost per area of inundation) with regard to the expected benefits, either quantitative or qualitative; and

for constraint measures, the information provided will be used to assess cost effectiveness with regard to other proposed constraint measures.

4.10.2 Projects not seeking Commonwealth Supply or Constraint Measure Funding

For projects that are not seeking Commonwealth Supply or Constraint Measure Funding (e.g. projects that have secured or will secure funding from other sources), it will only be necessary to provide a summary of costs.


The business case will be assessed on the basis that it provides:

a summary of costs or references to costing documentation;

details of funding arrangements;

details of ongoing operation and maintenance costs (including proposed financial responsibility for ongoing asset ownership costs and the agency which will undertake this role); and

a description of the expected benefits (environmental, social and economic benefits, quantitative where possible, otherwise described qualitatively).

4.11 Project Governance and Project Management Arrangements

If relevant, the business case needs to describe project management arrangements. In general, adherence to a State Government project management standards and guidelines would be considered appropriate if adequately described in the business case.

Existing projects or projects under development that are not seeking Commonwealth Supply or Constraint Measure Funding are not required to address section 4.11 of the guidelines. However, it is expected that the proponent will have independently taken responsibility for implementing appropriate stakeholder engagement, including ongoing stakeholder engagement on the operation of the regime, risk management and met all regulatory responsibilities.

4.11.1 Stakeholder management strategy

The business case needs to provide:

a comprehensive list of stakeholders;

an analysis of issues and sensitivities; and

an engagement and communication strategy that details:

o the consultation processes entered into for business case development and the outcomes, including whether there is broad community support;

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o what other consultation and communication will be undertaken during implementation including proposed timeframes; how information will be relayed (e.g. format, language, logistics, style); how feedback will be sourced; and how the consultation outcomes will be considered and responded to;

o any assumptions made during the identification of stakeholders and the development of the strategy; and

o a list of constraints that may affect consultation (e.g. time available, resources, availability of stakeholders).

The business case needs to provide sufficiently detailed information that could allow an independent assessment of the proponent’s engagement with stakeholders.


The business case will be assessed by SDLAAC on the basis that:

key stakeholder groups have been identified;

those materially affected have been consulted;

the consultation strategy will meet stakeholder expectations and respond to their concerns; and

there is evidence of broad community support for the project.

4.11.2 Legal and regulatory requirements

The business case needs to provide:

details of regulatory or legal requirements, including but not limited to:

o agreements with environmental water holders / water regulators;

o agreements with affected landholders; and

o regulatory approvals including Commonwealth, state and local government planning, environmental and heritage regulations.

details of legislative and policy amendments required, including but not limited to:

o water sharing frameworks;

o river operations rules or practices;

o the Murray‒Darling Basin Agreement; and

o state legislation.

a desktop cultural heritage assessment;

details of any required inter-jurisdictional agreement including the relationship of the project to any other BOC-led processes (requirement of cl.20(b) IGA Protocol); and

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details of the project’s requirements for environmental water, including details of long-term agreements in place with the Commonwealth Environmental Water Holder (CEWH) or any agreements required to be established (cl.20(c) IGA Protocol).

The business case needs to include a management strategy for each of the items listed above, detailing:

steps already undertaken;

the processes required;

timeframes;

risks and possible impediments; and

roles and responsibilities.

The business case needs to provide sufficiently detailed information that could allow an independent assessment of the measure.

The business case needs to provide certainty that the project will be undertaken to a standard that will allow successful completion of the measure and its operation as part of the SDL adjustment mechanism.


The business case will be assessed by SDLAAC on the basis that it provides the information requirements listed above and an appropriate management strategy for each.

4.11.3 Governance and project management

The business case needs to provide details of the governance and project management arrangements which will be used to ensure that the measure is delivered on time, within budget and against all key objectives. For example:

project management structure and team;

procurement strategy;

project steering committees or related governance mechanisms;

monitoring and reporting during implementation; and

design and implementation plan with timelines (Gantt Chart or similar).

The business case needs to provide sufficiently detailed information to allow an independent assessment of the governance and project management arrangements. Governance structures detailed in the business cases need to have appropriate senior management oversight of project management arrangements to allow successful completion of the measure and its operation as part of the SDL adjustment mechanism.


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The business case will be assessed by SDLAAC on the basis that it provides the information requirements listed above.

4.11.4 Risk assessment of Project Development and Delivery

The business case needs to include a risk assessment and risk management strategy for risks to project development and delivery.2 The risk assessment needs to identify risks and then rate them based on the likelihood (probability of occurrence) and consequence (magnitude of potential impact) of each risk. Appendix 8 provides a non-exhaustive list of the categories of risk that should be considered. The identification of risks needs to be rigorous and should not be limited by this list of categories.

The business case needs to provide certainty that the criterion will be met to a standard that will allow successful completion of the measure and its operation as part of the SDL adjustment mechanism.

The business case needs to provide sufficiently detailed information (i.e. quantitative or semi-quantitative) that could allow an independent assessment of the risks inherent in the project.



all significant project development and delivery risks and impacts have been identified, adequately described and analysed and robust treatments and mitigations proposed;

the risk management strategy complies with the AS/NZS ISO 31000:2009 Risk management—Principles and Guidelines; and

all residual risks are negligible or can be adequately mitigated.

2 Detailed requirements for identification and mitigation of ecological and water quality risks that arise as a result of the operation of the project as a supply measure is covered in section 4.7.

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Appendix 1: Expected steps and timeframes to develop and assess business cases

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Appendix 2: Diagram of assessment process after submission of business case to SDLAAC

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Appendix 3: Sustainable Diversion Limit adjustment mechanism governance diagram

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Appendix 4: Purposes of the Water for the Environment Special Account (s.86AD Water Act 2007)

(1) This section sets out the purposes of the Water for the Environment Special Account.

(2) Amounts standing to the credit of the Water for the Environment Special Account may be debited for any of the following purposes:

(a) making payments in relation to projects whose aim is to further the object of this Part by doing one or more of the following:

(i) improving the water efficiency of the infrastructure that uses Basin water resources for irrigation;

(ii) improving the water efficiency of any other infrastructure that delivers, stores or drains Basin water resources for the primary purpose of providing water for irrigation;

(iii) improving or modifying any infrastructure (including bridges and roads) that constrains the delivery of environmental water to the environmental assets of the Murray‒Darling Basin in order to ease or remove those constraints;

(iv) better utilising existing dams and storages to deliver environmental water to the environmental assets of the Murray‒Darling Basin;

(v) entering agreements to acquire an interest in, or in relation to, land (including easements) to facilitate environmental watering of the environmental assets of the Murray‒Darling Basin; and

(vi) improving the rules, policies, practices and procedures in relation to the use and management of the Basin water resources.

(b) purchasing water access rights in relation to Basin water resources for the purpose of furthering the object of this Part;

(c) making any other payments:

(i) in relation to projects whose aim is to further the object of this Part; or

(ii) to address any detrimental social or economic impact on the wellbeing of any community in the Murray‒Darling Basin that is associated with a project or purchase referred to in paragraph (a) or (b) or subparagraph (c)(i) so as to offset any such impact;

(d) meeting the expenses of administering the Account.

Note 1: As a result of subsection (4) of this section, water access rights may be purchased only if the purchase is related to an adjustment of a long-term average sustainable diversion limit under section 23A. That section requires the Basin Plan to prescribe criteria in relation to such adjustments. The effect of the criteria prescribed by the Basin Plan is that water access rights may be purchased only in conjunction with improving irrigation water use efficiency on farms or an alternative arrangement proposed by a Basin State.

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Note 2: Under this Part, the Commonwealth will not conduct open tender rounds that are available to all water access entitlement holders in a water resource plan area to purchase water access rights.

(3) For the purposes of this section, the expenses of administering the Water for the Environment Special Account do not include the cost of salaries of the Department.

(4) An amount may be debited from the Water for the Environment Special Account for the purpose of making a payment in relation to a project or purchase referred to in paragraph (2)(a) or (b) or subparagraph (2)(c)(i) only if the project or purchase is related to an adjustment of a long-term average sustainable diversion limit for the water resources of a particular water resource plan area (or a particular part of those water resources) under section 23A (whether or not the adjustment has been proposed, and whether or not the adjustment has been adopted as an amendment) because the project or purchase achieves the object of this Part in accordance with subsection 86AA(3).

Note: A proposed adjustment may be adopted by the Minister as an amendment of the Basin Plan under subsection 23B (6).

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Appendix 5: Summary of eligibility criteria and information requirements for developing and assessing business cases Eligibility criteria

Section Section guidelinesEnvironmental works

and measures at point locations

Water efficiency projects

Operating rules changes

Physical constraint measures

Operational and management

constraint measures

3.1 Supply measure requirements X X X

3.2 Constraint measure requirements X X

3.3 Operational by 30 June 2024 X X X X X

3.4.1 The measure is a ‘new measure’ Measures seeking Commonwealth funding

only

Measures seeking Commonwealth

funding only


funding only


funding only


funding only

3.4.2 Compliance with the purposes of the Water for the Environment Special Account


funding only


funding only

Information requirements3







constraint measures

4.1 Project details X X X X X

4.2 Ecological values of the site X X X X X

4.3 Ecological objectives and targets X X X X X

4.4 Anticipated ecological outcomes X X X X X

4.5 Hydrology of the area and environmental water requirements

X X X X X

4.6 Operating regime X X X X X

4.7 Assessment of risks and impacts of operating regime

X X X X X

3 For sections 4.2 to 4.7, not all requirements may be relevant for all projects. However it is recommended that all requirements are considered and where not relevant this is stated in the business case with the associated rationale.

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constraint measures

4.8 Technical feasibility and fitness for purpose X X X X X

4.9 Complementary actions and interdependencies X X X X X

4.10.1 Costs, benefits and funding arrangements for new unfunded projects

Measures seeking Commonwealth funding

only


funding only


funding only


funding only


funding only4.10.2 Costs, benefits and funding arrangements for

other projectsAll projects that did not

answer 4.10.1All projects that did not answer 4.10.1

All projects that did not answer 4.10.1



4.11 Project governance and project management arrangements

New measures only New measures only New measures only New measures only New measures only

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Appendix 6: Summary of key evaluation criteria

Key evaluation criteria Key evaluation criteria Guidelines reference

Eligibility The business case should indicate that the measure meets each relevant eligibility criterion for the category of project.

Section 3

Project details All business cases need to provide an overview of the project that contains, as a minimum, the following:

• description of proposed measure, including locality map;

• name of proponent and proposed implementing entity;

• summary of estimated costs and proposed schedule; and

• definition of the measure within one of the follow categories:

o environmental works and measures at point locations;

o water efficiency projects;

o operating rules changes;

o physical constraint measures; or

o operational and management constraint measures.

Section 4.1

Ecological values of the site

The business case will be assessed on the basis that the description of the ecological values and features of the site is:

• of a similar standard to the descriptions of ecological values and features found in Environmental Water Management Plans for Living Murray Icon Sites; and

• supported by relevant information from investigations of the site, including from published and unpublished scientific studies; environmental management plans; environmental water requirement reports; flora and fauna databases including those for threatened species; surveys; maps; and photos.

Section 4.2

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Ecological objectives and targets

The business case will be assessed on the basis that the ecological objectives and targets provided:

• are clearly articulated;

• represent the ecology of the site;

• are consistent with the Basin Plan (e.g. they reflect the objectives and targets in the Basin Plan, and supporting documentation, and are supported by scientific evidence); and

• are quantified where it is appropriate to do so;

• take into account interaction and inter-dependencies with other supply measures (to the extent possible prior to modelling by the MDBA that combines proposals);

• take into account ecosystem function, connectivity, interaction and inter-dependencies with other sites/habitats across the reach;

• are supported by evidence such as scientific reports, surveys, mapping/modelling;

• compare the frequency, extent and duration of watering of the proposed measures with:

o the natural regime; and

o under the Basin Plan without measure.

Matters to be considered in the assessment include:

• the overarching objectives in Schedule 7 of the Basin Plan;

• the site-specific objectives and targets listed in Appendix D of The proposed ‘environmentally sustainable level of take’ for surface water of the Murray–Darling Basin: Method and outcomes (November 2011) (ESLT report); and

• other work to develop ecological objectives and targets (e.g. development of objectives and targets for priority environmental assets in State long-term watering plans under cl.8.19 of the Basin Plan).

Section 4.3

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Anticipated ecological benefits

The business case will be assessed on the basis that it:

• includes an ecological assessment that is detailed enough to provide a clear picture of the likely ecological benefits of the project, including some quantitative assessment where this is possible (e.g. estimate of additional area inundated for different ecosystem components; e.g. expected number of additional inundation events); and

• is supported by relevant investigations, scientific studies, environmental management plans, and flora and fauna databases etc.

Section 4.4.1

Potential adverse ecological impacts


• an adequate assessment of potential adverse ecological impacts has been undertaken; and

• there is a demonstration that any adverse impacts can will be managed, mitigated or are managed to acceptable levels.

Section 4.4.2

Current hydrology and proposed changes to the hydrology

The business case will be assessed on the basis that SDLAAC can understand:

• the hydrology and hydraulic relationships at the site (if relevant);

• the volume of water used by the environment at the site;

• the proportion of environmental water that returns to the river under current conditions;

• the changes in flows that result from the proposal (where the proposal alters river flows);

• the scale and level of detail of modelling is fit-for-purpose (and in the case of inadequacy of data, that the uncertainty of the estimates is quantified);

• the assumptions used to represent the measure in the relevant model are documented; and

• supporting evidence shows that the model is calibrated adequately.

Section 4.5.1

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Environmental water requirements

The business case will be assessed on the basis that the environmental water requirements:

• are supported by scientific evidence;

• are linked to the ecological values at the site and the objectives and targets described in the business case; and

• the frequency at which different vegetation types will be inundated and the period of inundation can be clearly understood.

Examples of accepted practice for describing environmental water requirements can be found in the Living Murray Icon site Environmental Water Management plans.

Section 4.5.2

Operating regime The business case will be assessed on the basis that:

• it clearly describes the ecological justification for the operating regime;

• the operating regime includes a brief explanation of the role of each major structure followed by the operating scenarios;

• it lists the preferred timings for events and the main outcomes (e.g. land inundated, environmental water used);

• it provides an explanation of how the new measures will be operated in relation to existing scenarios; and

• it provides sufficient information to allow SDLAAC to evaluate the policy or rule change and identify key interdependencies (if relevant).

This should include explanation of how the structure will be operated to manage risks and to avoid or manage any adverse impacts.

Section 4.6

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Assessment of risks and impacts of the operation of the measure


• all significant operating risks and impacts have been identified and analysed, and robust treatments and mitigations proposed;

• the risk management strategy complies with the AS/NZS ISO 31000:2009 Risk management—Principles and Guidelines; and

• all residual risks are negligible or can be adequately mitigated.

Section 4.7

Technical feasibility and fitness for purpose


• the proposal is able to deliver effectively on its stated outcomes and any proposed technology is assessed to perform as intended; and

• the project delivery and operation is secure over the long term.

SDLAAC members will review the information provided and, if necessary, seek advice from other experts.

Section 4.8

Complementary actions and interdependencies

The business case will be assessed on the basis that known complementary actions and interdependencies are identified, noting that some interdependencies will only become clear once the project is modelled as part of package of measures.

Section 4.9

Costs, Benefits and Funding Arrangements for new unfunded projects seeking Commonwealth Supply or Constraint Measure Funding


• justification is provided in the business case that supports the rationale for the estimate of the total cost of the project;

• the level of contingency appears consistent with the level of risk identified (see section 4.7 and 4.11.4);

• for supply measures, the information provided will be used by SDLAAC to assess cost effectiveness (surrogates may be used in this analysis – e.g. cost per area of inundation) with regard the expected benefits, either quantitative or qualitative; and

• for constraint measures, the information provided will be used to assess cost effectiveness with regard to other proposed constraint measures.

Section 4.10.1

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Costs, Benefits and Funding Arrangements for Projects not seeking Commonwealth Supply or Constraint Measure Funding

The business case will be assessed on the basis that it provides:

• a summary of costs or references to costing documentation;

• details of funding arrangements;

• details of ongoing operation and maintenance costs (including proposed financial responsibility for ongoing asset ownership costs and the agency which will undertake this role); and

• a description of the expected benefits (environmental, social and economic benefits, quantitative where possible, otherwise described qualitatively).

Section 4.10.2

Stakeholder management strategy

The business case will be assessed by SDLAAC on the basis that:

• key stakeholder groups have been identified;

• those materially affected have been consulted;

• the consultation strategy will meet stakeholder expectations and respond to their concerns; and

• there is evidence of broad community support for the project.

Section 4.11.1

Legal and regulatory requirements

The business case will be assessed on the basis that it provides the information requirements listed at Section 4.11.2 and an appropriate management strategy for each.

Section 4.11.2

Governance and project management

The business case will be assessed on the basis that it provides the information requirements listed at Section 4.11.3.

Section 4.11.3

Risk assessment of Project Development and Delivery


• all significant project development and delivery risks and impacts have been identified, adequately described and analysed and robust treatments and mitigations proposed;

• the risk management strategy complies with the AS/NZS ISO 31000:2009 Risk management—Principles and Guidelines; and

• all residual risks are negligible or can be adequately mitigated

Section 4.11.4

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Appendix 7: Guidance on information required to support modelling and analysisNote: The information required will vary depending on the type, scale and complexity of each proposal. This appendix is for guidance only. If required, further advice on the information needed to support modelling should be sought from the SDLATWG or the MDBA.

Environmental works and measures at point locations: these infrastructure-based measures attempt to directly achieve the Basin Plan’s environmental outcomes at specific sites along the river using less environmental water than would otherwise be required.

Hydrology of the area and area of inundation (pre- and post-implementation)

Phase 2 Business Case Guidelines reference

Information to support modelling and analysis. This information will assist the MDBA or proponents represent a proposal in its hydrologic model(s)

Guidance on the standard of information required




Quantitative description of the hydrology and hydraulic relationships at the site.

The area of the works site that is inundated under various river flows conditions:

o currently; ando with the proposed works.

A comparison between the volume of water that returns to the river under current conditions and under the proposed works.

Where a proposal changes flows, a comparison of the flows under current conditions and the flows that result from the proposed changes.

Digital elevation model, cross sections and local data, if available. Vegetation layers, satellite images and other information to improve the

model’s calibration. Rainfall, evaporation and seepage loss rates for the site. Information on the antecedent conditions that may influence hydrology

and assessment of impacts. Spatial representation of area inundated and vegetation types

impacted for different levels of inundation at the site. Frequency at which different vegetation types would be inundated and

period of inundation. A description of any complementary actions, interactions and

interdependencies with any other works or measures or policy changes.

Adequate details to make robust assessment of the water savings possible under hydrological regime of 1895 to 2009 period.

The quality and quantity of data available and any issues that may affect any analysis or assessments - now or in the future – needs to be identified and documented.

Modelling needs to be fit-for-purpose. Where there is inadequate data, the

uncertainty of the estimates need to be quantified.

Information should be based on best available science, and include qualifiers – such as assumptions used which may affect modelling outcomes.

Spatial representation at a scale which is adequate to enable the assessment of the likely SDL reduction using ecological elements method.

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Details of proposed environmental works and measure




4.1 Project details 4.3 Ecological

objectives and targets

4.6 Operating regime 4.8 Technical

feasibility and fitness for purpose

A description of the proposed works or measures (e.g. regulators, levees, land use changes, changes in watering regimes etc).

Information about how the structures will be operated in order to meet the ecological objectives and targets.

Details of the works (e.g. sill levels, overtopping level, bed level etc). Adequate details of proposed works and measures to assist

assessment of hydrological impact under hydrology of 1895 to 2009 period.

Proposed operating rules for the works and measures under full range of hydrological conditions experienced during 1895 to 2009 period, including any risk mitigation strategies.

A description of the objectives and targets of the works align with the hydrological indicator site flow targets.

Design parameter values are adequate and detailed designs of works and measures are not needed.

The information related the operating regime should be detailed enough to include:

- Frequency of operations;- Minimum flow requirement at

river to operate works if any;- Equivalent natural flow at river

that leads to similar environmental outcomes at sites; and

- Inlet or outlet constraints if any.

Data analysis/modelling undertaken




4.5.1 Current hydrology and proposed changes to hydrology

Details of observed data or modelling undertaken (hydrologic/hydrodynamic) to assess current and changed hydrology of the system and consequent environmental outcomes or additional inundation area.

Details of representation of the proposed works and measures in the river system models.

Details of the calibration and validation carried out, if relevant. Fit-for-purpose hydrodynamic modelling or data analysis undertaken to

assess environmental outcomes or additional inundation area and change in hydrology under the long term climatic conditions of 1895 to 2009 period.

The scale and level of detail of modelling is fit-for-purpose and commensurate with the scale and complexity of the works.

If a model is used, supporting evidence showing that the model is calibrated adequately.

Mike 11/Mike Flood or similar software should be used.

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Water efficiency regulators: These infrastructure-based measures achieve water savings by reducing water losses through, for example, modified wetland or storage management. A hydrodynamic model may not be necessary to define the filling and emptying of a wetland or waterbody with river flow or height. This is largely dependent on the complexity of the proposal.

Hydrology of the area and area of inundation (pre- and post-implementation)






A description of the relationship between river flow and flow to the site. Storage-volume-area relationship for the site. Description of the volume of water that would remain at the site

compared to that which returns to the river. Rainfall, evaporation and seepage loss rates for the site Antecedent conditions that may influence hydrology and assessment of

impacts. Digital elevation model and local data, if available. Spatial representation of area inundated and vegetation types

impacted for different levels of inundation at the site. Frequency at which different vegetation types would be inundated and

period of inundation.


The quality and quantity of data available and any issues that may affect any analysis or assessments now or in the future – needs to be identified and documented.

Modelling needs to be fit-for-purpose. Where there is inadequate data, the

uncertainty of the estimates need to be quantified.

The level of information required is directly correlated to the complexity of the proposal.

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Details of proposed environmental works and measure




4.1 Project details 4.6 Operating regime 4.8 Technical

feasibility and fitness for purpose

A description of the proposed works regulators to control flow to wetlands/billabongs.

Details of the works (e.g. sill levels, overtopping level, bed level etc) Adequate details of proposed works and measures to assist

assessment of hydrological impact under hydrology of 1895 to 2009 period, including any risk mitigation strategies.

Proposed operating rules for the regulators under full range of hydrological conditions experienced during 1895 to 2009 period.

Design parameter values are adequate and detailed designs of works and measures are not needed.

The level of information required is directly correlated to the complexity of the proposal.






Details of observed data or modelling undertaken (hydrologic/hydrodynamic) to assess current and changed hydrology of the system and consequent water savings.

Details of representation of the proposed works and measures in the river system models. Calibration and validation carried out.

The scale and level of detail of modelling is fit-for-purpose and commensurate with the scale and complexity of the change.

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Operating rules changes: Changes to policies and operating rules can lead to more efficient use of water and savings which can contribute to achieving equal environmental outcomes with less water; and

Operational and management constraint measures: These measures change river management practices (e.g. policies, procedures and protocols that are outlined in legislation, intergovernmental agreements, water resource plans, river operating manuals and procedures and guidelines, as well as unwritten practices) that currently act as constraints on the capacity to deliver environmental water.

Current and proposed changes to operating policies and rules




4.1 Project details 4.7 Assessment of

risks and impacts of operating regime

4.8 Technical feasibility and fitness for purpose


A description of the current policies and proposed policies/operating rules under full range of hydrological conditions of 1895 to 2009 conditions.

A description of the third party impacts of the proposed changes and mitigation strategies.

A description of any complementary actions, interactions and interdependencies with any other works or measures or policy changes.


The quality and quantity of data available and any issues that may affect any analysis or assessments - now or in the future – needs to be identified and documented.

Modelling needs to be fit-for-purpose. Information about third party impacts,

complementary actions, interactions and interdependencies and risks should be supplied in accordance the requirements set out in these guidelines.

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Details of environmental outcomes and area of inundation (under current and changed policy settings)




4.4 Anticipated ecological outcomes4.5.1 Current hydrology and the proposed changes to the hydrology


A description of the change in hydrological regime and environmental outcomes for the hydrological indicator sites and baseflows in the system.

A description of the change in losses, end of system flows or water quality targets as specified in Basin Plan.

Environmental impact on downstream river systems in case of proposals for tributary valleys.

Spatial representation of area inundated and vegetation types impacted for different levels of inundation along the river system as well downstream river system - if the proposal is for a tributary valley.

Frequency at which different vegetation types would be inundated and period of inundation.







Details of data analysis or modelling undertaken to assess current and changed hydrology of the system and likely SDL reduction.

Details of representation of the proposed policy changes in models, testing of changes, assumptions or simplifications needed to represent the policy change.


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Appendix 8: Categories of risk and impact that should be considered in business case development

The types of risks and impacts to consider in the business case include (but not limited to):

Project development and delivery

These include:

design risks; risks to project completion on time; the risk of project failure; and the inability to deliver the project within budget.

For example, geo-technical risks; the nature of and extent to which the project relies on other proposed adjustment or constraint measures to achieve successful outcomes; and the nature of and extent to which other complementary actions are needed for the project to be successful.

Legal and landholder

These include:

the risks associated with gaining landholder agreements (e.g. agreements to flood land); risks of any impacts to landholders; and risks associated with gaining statutory approvals, changes to legislation and/or delays due to

parliamentary processes.

Cumulative impacts

These include the risks associated with the flow-on effects of implementing the project and the collective impacts of interactive measures. This includes possible impacts on state water shares and other States’ water resources.

Environmental/Ecological

The risks associated with accurately understanding, predicting and delivering ecological objectives at the site, within the reach and to downstream locations. These include risks to: fish (e.g. carp infestation, altered fish passage); vegetation (e.g. overwatering of red gums, promotion of exotic flora); bird breeding events; ecological communities; connectivity and ecological function; monitoring and evaluation; associated land management; and geomorphology and erosion.

These should consider the risks associated with effects on in-river flows or other sites other than the site at which the measure is proposed.

Salinity and water quality

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These include adverse salinity impacts (both real-time and long term salinity impacts), blue-green algae events and blackwater events.

Risks should include risks to the site, in-river risks and risks to downstream areas.

Cultural heritage

These include ongoing, as well as once off implications for significant sites, such as burial sites and scar trees and other elements identified through cultural heritage clearance.

Social and economic

These include stakeholder acceptance risks, downstream/third party impacts, access to parks for public use and pumping duration risks (e.g. conflicts with irrigator demands).

Modelling

Any risks associated with modelling (e.g. assumptions, accuracy of model, accuracy of input data, or interpretation of modelling outcomes).

Operation, maintenance and Management

Risks associated with the operation, maintenance and management of the measure post completion / commissioning, that may affect the enduring benefit of the measure, including any risks to projects that require future regulatory change.

This should also include ongoing monitoring, evaluation and reporting around the operation and ecological outcomes associated with the project.

Security of funds

Any risks that may affect the security of the funds sourced for the project to support project implementation into the future.

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Documents

Guidelines for supply and constraint measure …€¦ · Web viewPhase 2 Assessment Guidelines for Supply and Constraint Measure Business Cases Table of Contents APPENDICES3 ACRONYMS4